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Roma to Brisbane Pipeline – Dalby Compressor Station Upgrade Environmental Management Plan
PR104962-1 Rev 0; June 2011
Appendix 8
Noise Assessment
Roma to Brisbane Pipeline – Dalby Compressor Station Upgrade Environmental Management Plan
PR104962-1 Rev 0; June 2011
APA DALBY COMPRESSOR STATION
Proposed Extension
Environmental Noise Assessment
Prepared For
RPS 743 Ann Street, Fortitude Valley, Brisbane, QLD 4006.
S3551C2
January 2011
Sonus Pty Ltd 17 Ruthven Avenue
ADELAIDE SA 5000 Phone: (08) 8231 2100
Facsimile: (08) 8231 2122 www.sonus.com.au
ABN: 67 882 843 130
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 2
GLOSSARY
Background noise level Noise level in the absence of intermittent noise sources
Background creep The gradual increase in background noise levels in an area as a result
of successive developments generating constant noise levels at a
particular location.
CONCAWE The oil companies’ international study group for conservation of clean
air and water – Europe
“The propagation of noise from petrochemical complexes to
neighbouring communities”
dB(A) A weighted noise level measured in decibels. A weighting is a
frequency adjustment representing the response of the human ear
Equivalent noise level Energy averaged noise level
LA10 A weighted noise level exceeded 10% of the time, representing the
typical upper noise level
LA90 A weighted noise level exceeded 90% of the time, representing the
background noise level
LAeq A weighted equivalent noise level measured in decibels
LAeq, 1 hour A weighted equivalent noise level measured in decibels over a period
of 1 hour
LAeq, adj, 1 hour A weighted equivalent noise level measured in decibels over a period
of 1 hour and adjusted for tonality
LpA,LF Indoor low frequency A weighted noise level
RBL Rating Background Level
Sensitive receptor A location in the vicinity of the proposed development, where noise
may affect the amenity of the land use. For the proposed
development, sensitive receptors are generally dwellings.
Sound power level A measure of the sound energy emitted from a source of noise.
WHO World Health Organisation
Worst Case Conditions resulting in the highest noise level at or inside dwellings.
Worst case meteorological conditions can be characterised as no
cloud at night with wind from the project site to dwellings.
Worst case building construction refers to a façade constructed from
light weight materials providing the lowest noise reduction across it.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 3
TABLE OF CONTENTS
GLOSSARY ............................................................................................................................................ 2
TABLE OF CONTENTS ......................................................................................................................... 3
1 INTRODUCTION ............................................................................................................................. 4
2 DESCRIPTION OF EXISTING ENVIRONMENT ............................................................................ 5
3 METEOROLOGICAL CONDITIONS AND ATMOSPHERIC EFFECTS ........................................ 7
4 CRITERIA ..................................................................................................................................... 10
4.1 ENVIRONMENTAL PROTECTION (NOISE) POLICY 2008 ............................................................... 10 4.2 PLANNING FOR NOISE CONTROL GUIDELINE ............................................................................. 12 4.3 WORLD HEALTH ORGANISATION GUIDELINES ............................................................................ 13 4.4 LOW FREQUENCY NOISE DRAFT GUIDELINE .............................................................................. 13 4.5 SUMMARY OF CRITERIA ........................................................................................................... 14
5 ASSESSMENT.............................................................................................................................. 16
5.1 NOISE SOURCES ..................................................................................................................... 16 5.2 ADDITIONAL ACOUSTIC ATTENUATION ....................................................................................... 16 5.3 PREDICTED NOISE ................................................................................................................... 18
6 CONCLUSION .............................................................................................................................. 20
REFERENCES ...................................................................................................................................... 22
APPENDIX A: SENSITIVE RECEPTORS IN THE VICINITY OF THE FACILITY ............................... 23
APPENDIX B: NOISE CONTOUR ....................................................................................................... 24
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 4
1 INTRODUCTION
The APA Dalby Compressor Station is located near the township of Dalby. The APA Group
is proposing to extend the capacity of the facility involving the installation of two new
compression units.
Sonus has been engaged to make an assessment of the environmental noise from the
proposed extension to the Dalby Compressor Station. The assessment has consisted of:
a survey of the existing acoustic environment and equipment on site;
measurements of the noise from the existing compressor;
a prediction of the noise from the new compressors on site at the closest sensitive
receptors;
a comparison of the predicted levels with the relevant environmental noise criteria, and;
recommendations for acoustic treatment measures.
The new gas compression units will comprise a compressor and the associated drive
equipment. The gas compression units have the potential to operate continuously.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 5
2 DESCRIPTION OF EXISTING ENVIRONMENT
The Dalby Compressor Station is located near the township of Dalby. At sensitive receptors,
the acoustic environment is characterised by local and distant road traffic and natural noise
sources such as wind in trees and birds. This results in a low noise environment, typical of a
rural setting, except where a receptor is located in close proximity to the compressor station
or roads. Appendix A provides the coordinates and approximate distances of the sensitive
receptors considered in this assessment.
The topography between the site and the sensitive receptors is relatively flat and it is
expected that the topography will have negligible influence on the noise predicted at the
closest sensitive receptors.
Background noise levels (LA90) were measured at a location which was selected to be
indicative of nearby residences. The location was not influenced by any existing fixed noise
sources and was an equivalent distance to roads as most residences. The measurements
were made between the 18th and the 27th of October, 2010, in accordance with the
Queensland Department of Environment and Resource Management’s (DERM) “Noise
Measurement Manual” (the DERM Noise Measurement Manual).
Using the measurement data obtained, the Rating Background Levels (RBL) were calculated
in accordance with the “Planning for Noise Control” Guideline released by DERM. The
calculated RBLs are summarised in Table 2.1.
Table 2.1: Calculated Rated Background Levels.
RBL dB(A)
Day Evening Night
29 32 26
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 6
The RBL is determined from the lower tenth percentile of the LA90 noise level in the
environment and effectively represents the “lulls”. That is, the RBL is representative of the
quietest periods at the monitoring location. The calculated RBLs are considered to be
representative of all sensitive receptors which are located in an environment dominated by
distant traffic noise and natural noise sources such as wind in trees and birds.
Under certain conditions, an existing compressor unit located at the station can contribute to
the noise level at the sensitive receptors. Noise from the existing compressor was measured
in the vicinity of the site on the 22nd of October, 2010. These measurements were used to
estimate noise from the existing compressor at the sensitive receptors
As the RBL represents the lowest 10% of the LA90 noise level, existing noise sources will not
contribute to the RBL unless noise levels are significant during upwind conditions. To
determine the influence of the existing compressor on the RBL at each sensitive receptor,
predictions have been conducted under mild upwind conditions. Based on the predictions,
noise from the existing compressor only significantly influences the RBL at residence R1.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 7
3 METEOROLOGICAL CONDITIONS AND ATMOSPHERIC EFFECTS
The CONCAWE noise propagation model is used around the world and is widely accepted
as an appropriate model for predicting noise over significant distances.
The CONCAWE system divides the range of possible meteorological conditions into six
separate “weather categories”, from Category 1 to Category 6. Weather Category 1 provides
“best-case” (i.e. lowest noise level) weather conditions for the propagation of noise, whilst
weather Category 6 provides “worst-case” (i.e. highest noise level) conditions, when
considering wind speed, wind direction, time of day, and level of cloud cover. Weather
Category 4 provides “neutral” weather conditions for noise propagation.
For the purposes of comparison, Categories 1, 2 and 3 weather conditions are generally
characterised by wind blowing from the receptor to the noise source during the daytime with
little or no cloud cover. Category 4 conditions can be characterised by no wind and an
overcast day, whilst no wind and a clear night sky represent Category 5 conditions.
Category 6 conditions can be characterised by a clear night sky and wind blowing from the
noise source to the receptor.
In the particular circumstances of this development, it is noted that the noise levels
experienced at sensitive receptors in the vicinity of the facility will be significantly affected by
the weather category. For example, higher noise levels would be expected at sensitive
receptors with wind blowing from the site to the sensitive receptor (i.e. Category 5 or 6
conditions) than with wind blowing from the sensitive receptor to the site (i.e. Category 1, 2,
or 3 conditions).
Twelve months of historical meteorological data for Dalby were processed to determine the
likelihood of each meteorological category. The times during which the wind speed is greater
than 5m/s have been listed separately and excluded from each category, as it is anticipated
that ambient noise levels (from wind in trees) would mask the noise from the site at these
times.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 8
Tables 3.1 to 3.4 summarise the percentage of time in each meteorological category for the
closest sensitive receptor located to the north of the site (most critical receptor), and for
sensitive locations to the northeast, east and south of the site.
Table 3.1: Distribution of meteorological categories for sensitive receptor located to the north of the site.
Meteorological Category
Total Percentage of Time in Each Category
Percentage of Time in Each Category during Night-time Only
Wind Speed > 5m/s 16% 5%
Category 1 1% 0%
Category 2 10% 7%
Category 3 17% 16%
Category 4 24% 29%
Category 5 23% 28%
Category 6 9% 15%
Table 3.2: Distribution of meteorological categories for sensitive receptor located to the northeast of the site.
Meteorological Category
Total Percentage of Time in Each Category
Percentage of Time in Each Category during Night-time Only
Wind Speed > 5m/s 16% 5%
Category 1 2% 0%
Category 2 12% 8%
Category 3 26% 29%
Category 4 24% 35%
Category 5 12% 12%
Category 6 8% 11%
Table 3.3: Distribution of meteorological categories for sensitive receptor located to the east of the site.
Meteorological Category
Total Percentage of Time in Each Category
Percentage of Time in Each Category during Night-time Only
Wind Speed > 5m/s 16% 5%
Category 1 2% 0%
Category 2 13% 6%
Category 3 22% 28%
Category 4 25% 35%
Category 5 15% 15%
Category 6 8% 11%
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 9
Table 3.4: Distribution of meteorological categories for sensitive receptor located to the south of the site.
Meteorological Category
Total Percentage of Time in Each Category
Percentage of Time in Each Category during Night-time Only
Wind Speed > 5m/s 16% 5%
Category 1 1% 0%
Category 2 5% 1%
Category 3 18% 18%
Category 4 23% 27%
Category 5 22% 24%
Category 6 15% 25%
For compliance testing, the DERM Noise Measurement Manual requires that the noise
measurement be conducted during fine weather conditions with calm to light winds.
Measurement during conditions conducive to sound propagation should only be conducted if
the conditions are a true representation of the normal situation in the area. When conducting
a noise prediction, it is therefore considered appropriate that the prediction is also made for
fine weather conditions, unless conditions conducive to sound propagation are
representative of the normal conditions in the area.
To objectively determine whether the meteorological conditions conducive to sound
propagation are a representation of the normal conditions of an area, reference is made to
the Planning for Noise Control Guideline.
The Planning for Noise Control Guideline states that the meteorological conditions
conducive to sound propagation, such as temperature inversions (Categories 5 and 6) and
downwind conditions will be a significant feature of the area if they occur for 30% of the time.
Therefore based on Table 3.1, Categories 5 and 6 weather conditions are considered to be a
feature of the area at the most critical receptor.
Consequently, it is proposed that the assessment of noise at all sensitive receptors in the
vicinity of the facility be made under worst-case (CONCAWE Category 6) meteorological
conditions.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 10
4 CRITERIA
The Environmental Protection (Noise) Policy 2008 has been used as the primary method of
objectively assessing the noise from the proposal. However, reference is also made to the
World Health Organisation (WHO) Guidelines, the DERM “Planning for Noise Control”
Guideline and the DERM “Assessment of Low Frequency Noise” Draft Guideline.
4.1 Environmental Protection (Noise) Policy 2008
The Environmental Protection (Noise) Policy 2008 (the Policy) provides the management
intent to control background noise creep as well as achieve acoustic quality objectives for
sensitive receptors.
A traditional approach to environmental noise has been to measure existing background
noise levels1 prior to a development and to set environmental noise criteria at a certain level
above the existing background noise level. Where this methodology is used, background
noise levels are measured over a period of time to incorporate a range of meteorological
conditions. The background noise level used is at the lower end of the range of measured
levels.
One of the concerns about this methodology is that each development may increase the
background noise level allowing more relaxed criteria for future developments. This
theoretical phenomenon of the degradation of the acoustic environment with successive
developments is known as background creep. For this development to contribute to
background creep, successive developments would need to rely on background noise levels,
which have been elevated by previous projects, to set less stringent criteria.
1 For the purposes of this report the background noise level is represented by the RBL.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 11
To control background creep, the Policy includes:
To the extent that it is reasonable to do so, noise from an activity must not be –
(a) For noise that is continuous noise measured by LA90,T - more than nil
dB(A) greater than the existing acoustic environment measured by LA90,T;
or
(b) For noise that varies over time measured by LAeq,adj,T - more than 5 dB(A)
greater than the existing acoustic environment measured by LA90T.
As the noise from the proposal is expected to be continuous, it is part (a) that applies. Based
on the measured background noise levels, the criteria associated with controlling
background creep are shown in Table 4.1.
Table 4.1: Criteria to control background creep.
LA90,T dB(A)
Day Evening Night
29 32 26
Since the development of the WHO Guidelines, it has become more common for regulatory
authorities to base environmental noise criteria on avoiding health and wellbeing impacts
rather than comparison with background noise levels. The Policy includes acoustic quality
objectives based on the WHO Guidelines. These are described in Table 4.2.
Table 4.2: The Environmental Protection (Noise) Policy acoustic quality objectives.
Sensitive Receptor
Time of Day
Acoustic Quality Objectives (dB(A))* Environmental Value
LAeq,adj,1hr LA10,adj,1hr LA1,adj,1hr
dwelling (for outdoors)
daytime¹ and evening²
50 55 65 health and wellbeing
dwelling (for indoors
4)
daytime and evening
35 40 45 health and wellbeing
night-time³ 30 35 40 health and wellbeing in relation to the ability to sleep
Note: * Measured at the sensitive receptor. ¹ Daytime is defined by the Policy as “the period after 7am on a day to 6pm on the day”.
² Evening is defined by the Policy as “the period after 6pm on a day to 10pm on the day”. ³ Night-time is defined by the Policy as “the period after 10pm on a day to 7am on the next day”. 4 In accordance with the WHO Guidelines, indoor noise levels can be converted to outdoor levels by the addition of 15 dB(A) assuming windows being partially open for ventilation.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 12
The noise from the existing compressor is predicted to be 41 dB(A) at residence R1 under
worst case conditions. As the noise from the existing compressor dominates the noise level
at residence R1, it is not relevant to assess noise from the proposed compressors against
the RBLs at a location not influenced by the existing compressor. In accordance with the
intent of the Policy, the total noise from the site (including the existing and proposed
compressors) should achieve a level of 41 dB(A) in order to prevent background noise
creep.
4.2 Planning for Noise Control Guideline
At locations not influenced by industrial noise sources, the DERM Guideline specifies a
criterion based on the RBL, plus an adjustment of 3 dB(A) for the conversion to an
equivalent (LAeq) noise level. Therefore, based on the measured RBLs, the most stringent
(night time) criterion is 29 dB(LAeq) for residences R2-R9.
At locations where industrial noise sources are present, the DERM Guideline protects
against background noise creep by setting a criterion that results in no increase in the local
noise level. In situations where there is no opportunity to reduce existing noise levels, noise
from the proposed compressors should be limited to 10 dB(A) below any existing noise
source. However, it is expected that acoustic treatment incorporated in the expansion will
also reduce the noise from the existing compressor at residence R1. Under these
circumstances it is proposed that the total noise (existing and proposed compressors) from
the compressor station is to achieve the existing level of 41 dB(A), thereby achieving the
intent of the DERM Guideline.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 13
4.3 World Health Organisation Guidelines
The WHO has developed guidelines2 for community noise in specific environments. With
respect to annoyance, the guidelines state:
“To protect the majority of people from being seriously annoyed during the daytime, the
sound pressure level on balconies, terraces and outdoor living areas should not exceed
55 dB LAeq for a steady continuous noise. To protect the majority of people from being
moderately annoyed during the daytime, the outdoor sound pressure level should not
exceed 50 dB(A) LAeq.”
To avoid sleep disturbance, the WHO suggests that the equivalent noise level (LAeq) should
be limited to 30 dB(A) inside a bedroom at night. Based on the windows being partially open,
the WHO suggests that to achieve the internal level described above, the equivalent noise
level outside a bedroom window should be limited to 45 dB(A).
Sonus has conducted tests of the noise reduction achieved across the facade of a number of
dwellings. These tests include a range of facade constructions from light weight
transportable homes to masonry homes. The results of the testing indicate that with windows
partially open for ventilation, the noise transfer is typically around 15 dB(A). The tests
confirms that the WHO noise reduction of 15 dB(A) across a facade is appropriate.
4.4 Low Frequency Noise Draft Guideline
The noise from the proposed new equipment is not dominated by low frequency noise (refer
Table 5.1) but the propagation of sound over large distances attenuates the high and mid
frequencies, leaving a greater low frequency component and therefore as a conservative
approach, assessment against the suggestions of the Low Frequency Noise Draft Guidelines
has been included.
2 Berglund, Lindvall and Schwela, 1999, “Guidelines for Community Noise”
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 14
The draft guideline separates the assessment of low frequency noise based on the
frequency content of the noise and whether the noise is tonal or broad band. Based on
measurements of similar equipment at other sites, the noise experienced at sensitive
receptors will not include a significant component of infrasound (less than 20Hz) and will not
be tonal.
For non-tonal, low frequency noise in the range of 20Hz to 200Hz, the draft guideline
suggests that the noise is considered to be acceptable if the contribution of low frequency
noise within a sensitive receptor (LpA,LF) does not exceed 20 dB(A) during the evening or
night and 25 dB(A) during the day.
The low frequency noise transfer from outside to inside sensitive receptors varies
significantly based on the construction of the dwelling. Sonus has recently conducted tests of
the noise reduction achieved across the facade of a number of dwellings. The results from
these tests indicate that the low frequency noise reduction, with windows partially open,
ranges from 10 dB(A) for a light weight transportable home to 20 dB(A) for a well
constructed masonry home. This assessment has been based on a noise reduction of
10 dB(A), which represents a worst-case (conservative) assessment.
4.5 Summary of Criteria
The Policy, the DERM Guidelines and the recommendations of the WHO Guidelines have
been considered in determining appropriate criteria for the proposed extension.
It is common practice for noise from industrial sources to be predicted as an equivalent level
(LAeq), therefore the criteria provided in Table 4.1 require adjusting from the provided LA90
levels. A regularly accepted adjustment is an addition of 3 dB(A) for the conversion of an
LA90 to an LAeq noise level, an example of which is contained within the Planning for Noise
Control Guideline.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 15
With consideration to the existing ambient noise environment and the existing compressor
located on site, it is proposed that that the following criteria are established to ensure
compliance at each noise sensitive location:
Residence R1: Noise from both the existing and proposed compressors to achieve
an outdoor level of 41 dB(A); and,
Residences R2-R9: Noise from the proposed compressors to achieve a level of
29 dB(A).
Where the above criteria are achieved, the intent of the Environmental Protection (Noise)
Policy 2008, the World Health Organisation (WHO) Guidelines and the DERM Planning for
Noise Control Guideline will also be achieved.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 16
5 ASSESSMENT
5.1 Noise Sources
It is proposed that two Solar Centaur 50 compression units are to be installed at the Dalby
Compressor Station. Table 5.1 below contains sound power levels for each item of
equipment provided by the manufacturer of the compressors.
Table 5.1: Main noise sources and sound power levels
Noise Source
Maximum Sound Power Level (dB(A) re 1 pW) by Octave Band Frequency (Hz) Total
(dB(A)) 32 63 125 250 500 1000 2000 4000 8000
Unsilenced Combustion Air Inlet
68 87 103 111 118 123 127 151 141 151
Unsilenced Combustion Exhaust
79 94 104 110 123 120 115 103 92 125
Unenclosed Package
74 87 100 109 115 113 112 111 110 120
5.2 Additional Acoustic Attenuation
Noise from the operation of the new gas compression units at the sensitive receptors in the
vicinity of the site has been predicted using the CONCAWE noise propagation model in the
SoundPlan noise modelling software. The CONCAWE propagation model takes into account
topography, ground absorption and meteorological conditions, and has been used and
accepted around the world as an appropriate sound propagation model. In the noise model,
flat ground was considered as the attenuation due to undulating ground surface is
considered negligible at the closest sensitive receptor.
Based on the predicted noise from the proposed compressors it is required that additional
acoustic attenuation be applied to the standard measures included in Table 5.1. The
additional acoustic treatment is required to ensure compliance with the relevant criteria and
is summarised below:
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 17
Replace the standard inlet silencer with a silencer that provides an equivalent
acoustic performance to that provided in Table 5.2;
Replace the standard exhaust silencer with a silencer that provides an equivalent
acoustic performance to that provided in Table 5.2. A suitable example is a
“Colpro 750 series” silencer;
Enclose the package with the standard enclosure specified by the manufacturer,
such that the sound power levels provided in Table 5.2 are not exceeded;
Build an acoustic barrier from compressed fibre cement with a minimum thickness of
18mm, located no greater than 6m from the enclosed package. The barrier should
block line of sight between the enclosed package and the closest residence and be
at least 35m in length and a height of at least 1.5m above the height of the of the
enclosed package and air inlet. The barrier should be sealed airtight from the ground
to the full height of the barrier; and,
Acoustic insulation should be installed on the acoustic barrier described above. The
insulation should be 50mm thick with a minimum density of 32 kg/m3. This insulation
may be protected with a perforated material (such as sheet steel or fibre cement
sheeting) with an open area of at least 15%, a diagram of the proposed construction
is provided below.
Weatherproof capping
50mm thick acoustic insulation with a minimum density of 32 kg/m3
Perforated material (e.g. sheet steel, fibre cement sheet) with an open area > 15% spaced from the insulation to provide weatherproofing
Acoustic Barrier
Compressor Station Side
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 18
Table 5.2: Additional Acoustic Treatment.
Frequency (Hz) 31.5 63 125 250 500 1000 2000 4000 8000 Total
Inlet Silencer (Insertion Loss) (dB)
1 4 15 20 32 37 46 47 31 -
Exhaust Silencer (Insertion Loss) (dB)
- 21 32 39 51 48 46 39 31 -
Enclosed Package (SWL (dB(A))
65 79 87 95 97 96 93 89 82 102
Alternatively, the criteria could be achieved without the use of a barrier adjacent to the new
compressors by installing all three of the following additional measures:
An acoustic enclosure around the proposed compressors that performs significantly
better than the manufacturer’s standard enclosure;
An air inlet attenuator that performs significantly better than the manufacturer’s
standard attenuator;
Additional attenuation to the existing compressor, which may take the form of a small
barrier to block line of sight to the cooling fan.
5.3 Predicted Noise
The noise levels outside of dwellings R2-R9 have been predicted under worst case
meteorological conditions, from the operation of the new compressor units and the acoustic
treatment incorporating the noise barrier. The noise level at each sensitive receptor is
summarised in Table 5.3 and a noise contour is provided in Appendix B, based on the sound
power levels of the equipment listed in Table 5.1 and the additional acoustic attenuation
provided above.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 19
Table 5.3: Predicted Noise Level Outside the Dwellings.
Sensitive Receptor Predicted Noise Level (dB(A))
R2 28
R3 26
R4 23
R5 21
R6 18
R7 15
R8 16
R9 18
In addition, the low frequency noise level inside dwellings R2-R9 is below 20 dB(A).
Therefore, it is predicted that the compressor station will comply with the low frequency
noise draft guideline at each of these dwellings.
The noise level at residence R1 has been predicted under worst case conditions, due to the
simultaneous operation of the existing and proposed compressors. The total predicted noise
level from the compressor station is 40 dB(A), less than the existing noise level at residence
R1.
It is predicted that the low frequency noise level inside residence R1 from the operation of
the compressor station following installation is no greater than the level prior to the
extension.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 20
6 CONCLUSION
An assessment has been made of the noise from the proposed compressors at the APA
Dalby Compressor Station. The assessment considered noise from both the existing and
proposed compressors at the facility.
Based upon the Environmental Protection (Noise) Policy, appropriate conditions for noise
levels at sensitive receptors have been determined, taking into consideration the existing
acoustic environment. The proposed noise conditions for the operation of the facility are:
Residence R1: Noise from both the existing and proposed compressors to achieve
an outdoor level of 41 dB(A); and,
Residences R2-R9: Noise from the proposed compressors to achieve a level of
29 dB(A).
The noise at the sensitive receptors in the vicinity of the site from the operation of the
compressor station has been predicted. The predictions indicate that the proposed noise
conditions for the operation of the facility will be achieved at all sensitive receptors, with a
feasible level of acoustic treatment applied.
The acoustic treatment outlined in this report comprises:
Attenuators fitted to the air inlet and exhaust of the proposed compressors;
Enclosing the proposed compressors with a standard package specified by the
manufacturer; and
The construction of an acoustic barrier adjacent to the proposed compressors.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 21
Alternatively, the criteria could be achieved without the use of a barrier adjacent to the new
compressors by installing all three of the following additional measures:
An acoustic enclosure around the proposed compressors that performs significantly
better than the manufacturer’s standard enclosure;
An air inlet attenuator that performs significantly better than the manufacturer’s
standard attenuator; and,
Additional attenuation to the existing compressor, which may take the form of a
reduced barrier to block line of sight to the cooling fan.
With the above acoustic treatment in place, the APA Dalby Compressor Station will satisfy
the intent of:
The Environmental Protection (Noise) Policy 2008;
The World Health Organisation (WHO) Guidelines;
The DERM “Planning for Noise Control” Guideline; and,
The DERM “Assessment of Low Frequency Noise” Draft Guideline.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 22
REFERENCES
Berglund,B., Lindvall, T., and Schwela, D.H. 1999 . Guidelines for Community Noise. World Health Organisation, Geneva. DERM. 2004. Guideline – Planning for noise control. Department of Environment and Resource Management, Queensland Government, Brisbane, Queensland. DERM. 2002. Draft Guideline - Assessment of Low Frequency Noise. Department of Environment and Resource Management, Queensland Government, Brisbane, Queensland. Manning, C.J. 1981. The propagation of noise from petrochemical complexes to neighbouring communities. CONCAWE - The oil companies’ international study group for conservation of clean air and water – Europe. Queensland Government. 2009. Environmental Protection (Noise) Policy 2008. Reprint No.1. Queensland Government, Brisbane, Queensland. Queensland Government. 2000. Noise Measurement Manual. Third Edition. March. Environment Protection Authority, Queensland Government, Brisbane, Queensland.
APA Dalby Compressor Station Environmental Noise Assessment January 2011 S3551C2 PAGE 23
APPENDIX A: SENSITIVE RECEPTORS IN THE VICINITY OF THE FACILITY
Table A1: Coordinates and Approximates Distances of the Sensitive Receptors from the Site.
Sensitive Receptor
(WGS 84) Approximate Distance from the Site (m)
Easting Northing
R1 322576 6990902 350
R2 322315 6989262 1300
R3 323822 6990572 1300
R4 324091 6990755 1600
R5 324416 6991004 1900
R6 324350 6991185 1900
R7 324021 6991620 1800
R8 323709 6991752 1700
R9 323541 6991546 1400
Loction 1
A.1